Chemistry, taxonomy and ecology of the potentially chimpanzee-dispersed Vepris teva sp.nov. (Rutaceae) endangered in coastal thicket in the Congo Republic

Continuing a survey of the chemistry of species of the largely continental African genus Vepris, we investigate a species previously referred to as Vepris sp. 1 of Congo. From the leaves of Vepris sp. 1 we report six compounds. The compounds were three furoquinoline alkaloids, kokusaginine (1), maculine (2), and flindersiamine (3), two acridone alkaloids, arborinine (4) and 1-hydroxy-3-methoxy-10-methylacridone (5), and the triterpenoid, ß-amyrin (6). Compounds 1–4 are commonly isolated from other Vepris species, compound 5 has been reported before once, from Malagasy Vepris pilosa, while this is the first report of ß-amyrin from Vepris. This combination of compounds has never before been reported from any species of Vepris. We test the hypothesis that Vepris sp. 1 is new to science and formally describe it as Vepris teva, unique in the genus in that the trifoliolate leaves are subsessile, with the median petiolule far exceeding the petiole in length. Similar fleshy-leathery four-locular syncarpous fruits are otherwise only known in the genus in Vepris glaberrima (formerly the monotypic genus Oriciopsis Engl.), a potential sister species, but requiring further investigation to confirm this phylogenetic position. We briefly characterise the unusual and poorly documented Atlantic coast equatorial ecosystem, where Vepris teva is restricted to evergreen thicket on white sand, unusual in a genus usually confined to evergreen forest. This endemic-rich ecosystem with a unique amphibian as well as plants, extends along the coastline from the mouth of the Congo River to southern Rio Muni, a distance of about 1,000 km, traversing five countries. We map and illustrate Vepris teva and assess its extinction risk as Endangered (EN B1ab(iii)+B2ab(iii)) using the IUCN, 2012 standard. Only three locations are known, and threats include port and oil refinery construction and associated activities, with only one protected location, the Jane Goodall Institute’s Tchimpounga Reserve. Initial evidence indicates that the seeds of Vepris teva are dispersed by chimpanzees, previously unreported in the genus.


INTRODUCTION
As part of a series of studies of the chemistry of Vepris led by the first author, material from a Congolese Vepris previously referred to in field studies as Vepris sp. 1 of Pointe Noire was investigated. In this article we present the chemical results, compare the taxon morphologically within Vepris, test the hypothesis that this taxon is new to science and formally name it as Vepris teva Cheek. We also present data on its ecology in coastal thicket on white sand, a poorly known and highly threatened ecosystem on the equatorial Atlantic coast of Africa. Initial field observations suggest that the seeds of Vepris teva are dispersed by chimpanzees.
Vepris Comm. ex A. Juss. (Rutaceae-Toddalieae), is a genus with 91 accepted species, 23 in Madagascar and the Comores and 68 in Continental Africa with one species extending to Arabia and another endemic to India (POWO, continuously updated). The genus was last revised for tropical Africa by Verdoorn (1926). Founded on the Flore du Cameroun account of Letouzey (1963a), nine new species were recently described from Cameroon (Onana & Chevillotte, 2015;Cheek, Gosline & Onana, 2018a;Onana, Cheek & Chevillotte, 2019;Cheek, Hatt & Onana, 2021), taking the total in Cameroon to 25 species, the highest number for any country globally. The greatest concentration of Vepris species in Cameroon is within the Cross-Sanaga Interval (Cheek et al., 2001) with 15 species of Vepris of which nine are endemic to the Interval. The Cross-Sanaga has the highest species and generic diversity per degree square in tropical Africa (Barthlott, Lauer & Placke, 1996;Dagallier et al., 2020) including endemic genera such as Medusandra Brenan (Peridiscaceae, Breteler, Bakker & Jongkind, 2015;Soltis et al., 2007). By comparison, neighbouring Gabon has just eight species, seven species of Vepris listed in the Gabon checklist (Sosef et al., 2006) and V. lecomteana. (Pierre) Cheek & T. Heller. Meanwhile, just one species, Vepris lecomteana is listed for Congo-Brazzaville (POWO, continuously updated), illustrating how under-recorded the Flora of this biodiverse country is. However, it is almost certain that additional species for this country are represented in the Paris herbarium, P., but we have not been able to access this during the pandemic. Several Cameroon species are threatened (Onana & Cheek, 2011) and in one case considered globally extinct (Cheek, Gosline & Onana, 2018a), although only two currently appear on the IUCN Red List: Vepris lecomteana (Pierre) Cheek & T. Heller (Vulnerable, Cheek, 2004) and Vepris trifoliolata (Eng.) Mziray (Vulnerable, World Conservation Monitoring Centre, 1998). In other parts of Africa species are even more highly threatened, e.g., the Critically Endangered Vepris laurifolia (Hutch. & Dalziel) O. Lachenaud & Onana of Guinea-Ivory Coast (formerly V. felicis Breteler, Cheek, 2017;Lachenaud & Onana, 2021).
In continental Africa, Vepris are easily recognised. They differ from all other Rutaceae because they have digitately (1-)3(-5)-foliolate (not pinnate) leaves, and unarmed (not spiny) stems. The genus consists of evergreen shrubs and trees, predominantly of tropical lowland evergreen forest, but with some species extending into submontane forests and some into drier forests and woodland. Vepris species are often indicators of good quality, relatively undisturbed evergreen forest since they are not pioneers. New species are steadily coming to light .
Species of Vepris in Africa extend from South Africa, e.g., Vepris natalensis (Sond.) Mziray, to the Guinean woodland in the fringes of the Sahara Desert (Vepris heterophylla (Engl.) Letouzey). Mziray (1992) subsumed the genera Araliopsis Engl., Diphasia Pierre, Diphasiopsis Mendonça, Oricia Pierre, Oriciopsis Engl., Teclea Delile, and Toddaliopsis Engl. into Vepris, although several species were only formally transferred subsequently (e.g., Harris, 2000;Gereau, 2001;Cheek, Oben & Heller, 2009;Onana & Chevillotte, 2015). Mziray's conclusions were largely confirmed by the molecular phylogenetic studies of Morton (2017) but Morton's sampling was limited, identifications appeared problematic (several species appear simultaneously in different parts of the phylogenetic trees) and more molecular work would be desirable. Morton studied about 14 taxa of Vepris, all from eastern Africa. More recently Appelhans & Wen (2020) focussing on Rutaceae of Madagascar have found that the genus Ivodea Capuron is sister to Vepris and that a Malagasy Vepris is sister to those of Africa. However, the vast majority of the African species including all those of West and Congolian Africa, remain unsampled leaving the possibility open of changes to the topology of the phylogenetic tree when this is addressed.
Characteristics of some of the formerly recognised genera are useful today in grouping species. The "araliopsoid" species have firm, subglobose, four-locular fruit syncarpous with four external grooves; the "oriciopsoid" soft, fleshy four-locular syncarpous fruit; "oricioid" species are four-locular and apocarpous in fruit; the fruits of "diphasioid" species are laterally compressed in one plane, bilocular and bilobed at the apex; while "tecleoid" species are unilocular in fruit and one-seeded, lacking external lobes or grooves. There is limited support for these groupings in Morton's study, Due to the essential oils distributed in their leaves, and the alkaloids and terpenoids distributed in their roots, bark and leaves, several species of Vepris have traditional medicinal value (Burkill, 1997 (Burkill, 1997: 651-653). Research into the characterisation and anti-microbial and anti-malarial applications of alkaloid and limonoid compounds in Vepris is active and ongoing (e.g., Atangana et al., 2017), although sometimes published under generic names no longer in current use, e.g., Wansi et al. (2008). Applications include as synergists for insecticides (Langat, 2011). Cheplogoi et al. (2008) and Imbenzi et al. (2014) respectively list 14 and 15 species of Vepris that have been studied for such compounds. A review of ethnomedicinal uses, phytochemistry, and pharmacology of the genus Vepris was recently published by Ombito, Chi & Wansi (2021), listing 213 different secondary compounds, mainly alkaloids and furo-and pyroquinolines, isolated from 32 species of the genus, although the identification of several of the species listed needs checking. However, few of these compounds have been screened for any of their potential applications. Recently, Langat et al. (2021) have published three new acridones and reported multi-layered synergistic anti-microbial activity from Vepris gossweileri (I.Verd.) Mziray, recently renamed as Vepris africana (Hook.f ex Benth.) Lachenaud & Onana (Lachenaud & Onana, 2021).

Taxonomy
The electronic version of this article in Portable Document Format (PDF) will represent a published work according to the International Code of Nomenclature for algae, fungi, and plants (ICN), and hence the new names contained in the electronic version are effectively published under that Code from the electronic edition alone. In addition, new names contained in this work which have been issued with identifiers by IPNI will eventually be made available to the Global Names Index. The IPNI LSIDs can be resolved and the associated information viewed through any standard web browser by appending the LSID contained in this publication to the prefix "http://ipni.org/". The online version of this work is archived and available from the following digital repositories: PeerJ, PubMed Central, and CLOCKSS.
Fieldwork in the Republic of Congo resulting in the specimens and observations cited in this article was conducted with the collaboration and support of the CERVE (Centre  -3-490-6 (2010-2011). The most complete set of duplicates for all specimens made was deposited at IEC, the remainder exported to K for identification and distribution following standard practice.
The taxonomic study is based on herbarium specimens and observations of live material in Congo-Brazzaville made by the second two authors and their colleagues in 2010-2012. Herbarium citations follow Index Herbariorum (Thiers, continuously updated), nomenclature follows Turland et al. (2018) and binomial authorities follow IPNI (2021). The methodology for the surveys in which the specimens were collected is given in Cheek & Cable (1997). All specimens cited have been seen. Material of the suspected new species was compared morphologically with material of all other species African Vepris, principally at K, but also using material and images from BM, EA, BR, FHO, G, GC, HNG, P and YA. Specimens at WAG were viewed on the Naturalis website (https://bioportal. naturalis.nl/). The main online herbarium used during the study apart from that of WAG was that of P (https://science.mnhn.fr/all/search). Herbarium material was examined with a Leica Wild M8 dissecting binocular microscope fitted with an eyepiece graticule measuring in units of 0.025 mm at maximum magnification. The drawing was made with the same equipment using a Leica 308700 camera lucida attachment.

Ecology
Once Vepris teva was detected as being new to science, seemingly restricted to coastal white sands (with other new and threatened species) in July 2011 we conducted desk-top studies using Google Earth to find other areas of this poorly studied habitat where it survives in the Republic of Congo. We visited these areas in November-December 2012, travelling by road from the northern border with Gabon to the southern border with Angola (Cabinda) to visit targeted sites, but also ground-truthing sites in different but adjoining habitats to test whether the species was indeed restricted to the white sand habitat.

Chemistry
Samples were made from live plants (preferable to preserved material for chemical analysis) cultivated from seed at the Royal Botanic Gardens, Kew which were associated with the herbarium collections Mpandzou et al. 1754 (IEC, K) collected with the authorisation of Herbier National, Institut de Recherche National en Sciences Exactes et Naturelles (IRSEN formerly CERVE, see permit references below), Cité Scientifique de Brazzaville. Two plants, grown from seed, were cultivated in 3 inch (c. 8 cm) diam. plastic pots, using a free-draining potting medium of 25% Coir (coconut husk fibre), 17% each of Seramis (baked expanded clay granules), medium Perlite (amorphous volcanic glass) and fine bark, 12% loam and 12% grit, with a slow-release fertiliser. Plants were cultivated in a glasshouse in full light, with temperature maintained in the range 21-25 deg. Celsius. The humidity goal is 70%, achieved by spraying over and damping down the floor at least twice a day. Watering is usually once per day, and feeding twice a week in summer, once in winter, with an additional weekly Kelp feed.
The plants grew very slowly, reaching only 15 cm in height, and not becoming reproductive, even after 10 years of cultivation, before they died in 2021. The cause of death is unknown. This suggests that there is scope to develop an improved cultivation protocol. The RBG, Kew reference number for this accession was 2019-14.
Spectroscopic and spectrometric analysis were conducted as follows: the FTIR spectra were recorded using a Perkin-Elmer Frontier/Spotlight 200 spectrometer, and the acquired data used to determine the functional groups present in the compounds. 1D and 2D NMR spectra were recorded in CDCl 3 on a 400 MHz Bruker AVANCE NMR instrument at room temperature. Chemical shifts (δ) are expressed in ppm and were referenced against the solvent resonances at δ H 7.26 and δ C 77.23 ppm for 1 H and 13 C NMR for CDCl 3 . Accurate masses, for determination of molecular formulae of the compounds, were recorded on a Thermo Scientific Orbitrap Fusion spectrometer. Purity of compounds was monitored via thin layer chromatography (TLC) using pre-coated aluminium-backed plates (silica gel 60 F 254 ; Merck, Kenilworth, NJ, USA) and compounds were visualised by UV radiation at 254 nm and then using an anisaldehyde spray reagent (1% p-anisaldehyde:2% H 2 SO 4 :97% cold MeOH) followed by heating. Final purifications used preparative thin layer chromatography (Merck 818133) and gravity column chromatography that was carried out using a 2 cm diameter column, which were packed with silica gel (Merck Art. 9385) in selected solvent systems.
The leaves were freeze-dried and ground to fine powder using a blender. The dried leaves (37 g) were successively extracted using methylene chloride (CH 2 Cl 2 ) solvent to target non-polar and semi-polar compounds and methanol solvent (MeOH) to target polar compounds. The CH 2 Cl 2 and MeOH extracts obtained were 1.7 g and 4.3 g respectively. The methylene chloride extract was subjected to gravity column chromatography packed with a 1:1 blend of silica gel merck 9385 and eluted isocratically using 10% ethyl acetate in methylene chloride, collecting 35 mL. The fractions were monitored using TLC and fractions with the same retention times were pooled. Fractions 12-13 gave compound 5 which was determined to be 1-hydroxy-3-methoxy-10-methylacridone (Haensel & Cybulski, 1978). Fractions 14-18 gave compound 6 which was determined to be ß-amyrin (Okoye et al., 2014). Fractions 23-25 gave compound 2 which was determined to be maculine (Vaquette et al., 1976). Fractions 34-35 gave compound 4 which was determined to be arborinine (Haensel & Cybulski, 1978). Fractions 40-47 gave compound 3 which was determined to be flindersiamine (Vaquette et al., 1976) and fractions 55-63 gave compound 1 which was determined to be kokusaginine (Pusset et al., 1991).

Extinction risk assessment
Points were georeferenced using locality information from herbarium specimens. The map was made using simplemappr (Shorthouse, 2010). The conservation assessment was made using the categories and criteria of IUCN (2012), EOO was calculated with GeoCat (Bachman et al., 2011). Threats were observed by the second two authors directly in the field in Republic of Congo.
This combination of secondary compounds matches none of those reported from the 32 taxa of Vepris that have been chemically investigated to date (Ombito, Chi & Wansi, 2021). While compounds 1-4 are relatively widespread in the investigated species, each having been recorded in 9-12 taxa, compound 5 is recorded only in one species, Vepris pilosa (Baker)I.Verd. (now a synonym of V. glomerata (F.Hoffm.)Engl.). However, compounds 2 & 3 have not been recorded in Vepris glomerata. Compound 6 has not been reported previously from Vepris. The chemical results therefore do not conflict with the morphologically-based conclusion that Vepris sp. 1 is new to science (see below).

Morphology
The morphological characteristics of Vepris sp. 1 are highly unusual within the genus. The subsessile leaves of the fertile stems with the median petiolule far exceeding the petiolule in length is unique within the genus. The leathery-walled, syncarpous, fourloculed, and slightly lobed, subverrucate fruits which have fleshy-juicy mesocarp surrounding the seeds are otherwise known in only one species, Vepris glaberrima, formerly segregated as the monotypic genus Oriciopsis. The two species share several unusual characters, such as numerous parallel, straight secondary and intersecondary nerves, with few quaternary nerves, sparse oil glands and long median petiolules, suggesting they are sister species. Vepris sp. 1 however differs greatly from the last species in the characters indicated below in Table 1 and in the diagnosis below.   (2), and flindersiamine (3). Acridone alkaloids: arborinine (4) and 1-hydroxy-3-methoxy-10-methylacridone (5).

Ecology. The evergreen thicket ecosystem on white sand on the Atlantic coast of Africa
Vepris teva is restricted to the key vegetation type, thicket on white sand, that occurs in a coastal ecosystem extending along the equatorial Atlantic coast of Africa in the southern hemisphere. This ecosystem extends from the mouth of the Congo River in the Democratic Republic of Congo, along the coast through Angolan Cabinda, Republic of Congo into southern Gabon, with some areas thought to extend into Rio Muni of Equatorial Guinea. It extends discontinuously along the coastline for about 1,000 km and extends inland for between 100-3,000 m, and is based on old, partly dissected and flattened, highly leached white sand dunes that run parallel to the coast, alternating with lower, wet or seasonally wet drainage areas often developing black peaty soils, that can develop either swamp forest e.g., with Alstonia congensis Engl. trees and an understorey of Acrostichum aureum L. or a wetland grassland community including Cyperaceae, Utricularia, Drosera, Xyridaceae and Stipularia africana P.Beauv. Thicket develops on the top of the ridges. In the ecotone transition areas, the shallow slopes between the thicket and wetland area, a sparse grassland develops on the upper part of the white sand with Chlorophytum, Dissotis congolensis (Cogn. ex Büttner) Jacq.-Fél., Eulophia caricifolia (Rchb.f.) Summerh., and in the lower damper, seasonally inundated parts of the ecotone, grass species including Anadelphia hamata Stapf, and herbs such as Neurotheca corymbosa Hua, both globally restricted to this vegetation type.
On the seaward side of the dunes a sea-shore community including halophytes develops with succulent species such as Sansevieria longiflora Sims, while in brackish inlets the Atlantic mangrove community is formed, including Rhizophora racemosa G.Mey. On the landward side of the ecosystem two substrates interface with the white sand, red-brown loam, and grey sand which each have their own communities of grassland species. This ecosystem has rarely been referred to in the literature. The best account is probably that by Vande Weghe (2007)  The grassland is maintained by dry season fires which kill most or all woody plants (Vande Weghe, 2007), none of which, curiously, appear fire-adapted. Such grassland fires were recorded by us in Congo in July 2010. Owing to the sparsity of the herbs in the grassland, fires are not intense due to the low fuel-load. It is sometimes possible for shrubs to establish in grassland. Chrysobalanus icaco is a shrub which, once established, in the absence of fire, can spread laterally to form a thicket in which other species of shrub and tree can colonise, leading towards succession from grassland to thicket.
Among the endemic and highly threatened shrub species of this ecosystem, several apart from Vepris teva, were found to be new to science. Of these, those recently published are Dracaena marina Damen (Damen et al., 2018), Baphia vili Cheek , Salacia arenicola Gosline (Gosline, Cheek & Kami, 2014). However, several additional species remain to be published.
Local names and uses. None are recorded.
Etymology. Named for Teva Kami, lead collector of the type specimen, who played a key role in the discovery of this species and further research upon it concerning interactions with chimpanzees (see below).
Conservation. Vepris teva is known from nine specimens and seven sight-records made between July 2011-February 2012. These equate to an area of occupation of 40 km 2 using the IUCN-preferred 4 km 2 gridcells, and an extent of occurrence of 172 km 2 . It is restricted to coastal thicket on white sand habitat in Republic of Congo. This habitat is thought to extend along the Atlantic coast from coastal DRC to southern Equatorial Guinea. Despite targetted surveys in this habitat through most of this range especially in Congo, Vepris teva has only been found at three of the more than eight locations studied. These are: (1) Pointe Noire at Point Indienne; (2) Djeno; (3) Tchimpounga. At the first location, the plants are threatened by an extension northward of the port of Pointe Noire to accommodate export of rock phosphate, manganese, iron-ore for which there is currently insufficient port capacity. Plants of Vepris teva are also threatened by cutting of their coastal thicket habitat for charcoal and for clearance for housing. At the second location, plants are threatened by the infrastructure and activities of the Total E&P Congo petro-chemical plant (part of TotalEnergie S.A.), the installation of which appears to have destroyed much of the habitat of Vepris teva at this location. Indirectly, Total, as the major employer at Djeno attracting labour which requires local accommodation, appears to have stimulated an expansion of urbanisation, resulting in Vepris teva habitat being parcelled for sale as house building plots (M Cheek, 2012, personal observations). At Tchimpounga, a reserve created by the Jane Goodall Foundation to protect chimpanzees, Vepris teva uniquely appears protected and secure so long as this venture is supported. In view of the EOO and AOO, and the threats stated, we here assess Vepris teva as Endangered (EN B1ab(iii)+B2ab(iii)).
Notes. We first detected Vepris teva in July 2011, during the dry season environmental impact studies for a proposed new port facility near the major existing port of Pointe Noire, Congo's principal port and commercial centre. It was provisionally named as 'Vepris sp. 1 of Pointe Noire,' and considered likely to be new to science since it matched no other known species of the genus in tropical Africa (Cheek, van der Burgt & Pickering, 2010). Further collections were made in a wet season survey in November and December 2011. These surveys resulted in the discovery of many other rare species, usually previously unknown to science, mainly confined to evergreen thicket on coastal white sand. Consequently, surveys in November-December 2012 were made along the length of the Congolese coastline to map the full national extent of this ecosystem and of its rare and threatened species. It was discovered that unlike many of the coastal thicket species, Vepris teva is restricted to only a small length of the coast, from Djeno in the south to Tchimpounga in the north. At these three sites, wherever coastal thicket on white sand appears, Vepris teva can be fairly frequent. However, when thicket become degraded or damaged, it is no longer present. We believe that our surveys have detected all sites where this species survives in the Republic of Congo. However, it is possible that additional individuals might survive in fragments of original vegetation that were overlooked by us e. g., within the greater area of the city of Pointe Noire, but we consider this unlikely. Also, it is possible that the species might extend to Angola (Cabinda) or southern Gabon which we were not able to visit during the studies referred to in this article. Vepris teva sometimes grows alongside another species of the genus, Vepris africana (formerly Vepris gossweileri).
The two species cannot be confused since the first is trifoliolate, while the second is unifoliolate. No Vepris species other than these two have been found in coastal thicket on white sand in Congo. Our knowledge of the phenology of Vepris teva is restricted to two periods of the year -July (dry season) and November-December (wet season). At both seasons plants were found in both flower and fruit. All flowers collected are monomorphic and have well-developed stamens with pollen, and are therefore supposed to be male. This is supported by our observation that while the fruits (the undoubted products of female flowers) have a 1 mm diam. peltate, discoid stigma, peltate stigmas have not been in any of the flowers which are therefore male. Since Vepris species have been found to be dioecious wherever their reproductive strategies have been studied, we conclude that female flowers remain to be discovered, although female plants (in fruit) have been collected. There is a small possibility that Vepris teva, atypically in the genus, might have hermaphroditic flowers.
Vepris teva grows very slowly from seed. Three plants cultivated at the Royal Botanic Gardens, Kew from seed collected in 2011, reached only 15-25 cm tall after 5 years. By March 2020, after 8.5 years, the plants had reached 30-45 cm tall, but none had shown signs of flowering. All three of these plants showed the long petiole of sterile plants, and not the characteristic extremely short petioles of reproductive individuals. Thus, the age of sexual maturity is likely to be at least 10 years in Vepris teva.
Because Vepris teva has a 4-locular syncarpous flower producing a soft fleshy fruit it would formerly have been classified in the monotypic genus Oriciopsis Engl. (Engler, 1931), together with V. glaberrima (Letouzey, 1963b: 79-80). The last species occurs in lowland evergreen forest at the junction of Cameroon, C.A.R. and Gabon and is also a small, sparingly branched shrub. It is conceivable that the two are sister species (see above). Four-locular syncarpous ovaries are also seen in the formerly accepted genera Araliopsis and Toddaliopsis, but in these taxa the fruits are hard. The former occurs in W-C Africa but is a large tree with digitately 5-foliolate leaves, the second a tree of coastal E Africa with a subspiny, "nut-like" fruit.
Vepris teva appears unique and is easily recognisable in the genus and in its habitat because of the combination of long petiolules with extremely short petioles on the fertile stems. The petioles can be so contracted that they are almost invisible, and it then appears that there are three simple, leaves, each on its own petiole (in fact leaflets on petiolules) at each node.
Chimpanzee-mediated seed dispersal. During field surveys of the vegetation in which Vepris teva occurs, the last author tested the hypothesis that the fruits might conform to the 'spat seed' syndrome characteristic of some primate-dispersed plant species (Sengupta, McConkey & Radhakrishna, 2015;Dominy & Duncan, 2005). When the base of a fruit plucked from a shrub is sucked, the pleasantly sweet, watery mesocarp with the seed(s) enters the mouth, the juice can be swallowed, and the slippery seed(s) in their endocarp(s) spat out (Fig. 5).
One of the three known locations for Vepris teva is the Tchimpounga Reserve, co-managed by the Jane Goodall Institute (Jane Goodall Institute, 2018) which focuses on chimpanzee conservation and research of both rescued animals from captivity and hunting, and chimpanzees indigenous to the coastal thicket ecosystem (see below). During field observations for doctoral studies of fruit consumption by chimpanzees from tree species by the second author ( , Kami, 2021, chimpanzees were observed to seemingly feed on the fruits of this species of Vepris-evidenced by empty pericarps and separated, spat seeds of this species after they had been in the vicinity of the fruiting shrubs. Chimpanzee seed dispersal of Vepris teva seems very likely but more detailed studies are needed to confirm this.

CONCLUSIONS
The description of a known compound, ß-amyrin, for the first time in Vepris, is consistent with previous research wherein nearly each species of the genus that is newly chemically investigated contributes additional compounds, often those that are new to science (e.g., Langat et al., 2021). The number of species of Vepris that have been chemically investigated is rising steadily, numbers having doubled in the last 7 years, with 15 species of Vepris reported as investigated by Imbenzi et al. (2014) and 32 by Ombito, Chi & Wansi (2021), the last reporting 213 secondary compounds in five classes from Vepris. However, this represents only a third of the known species diversity of the genus, which itself is increasing as taxonomists uncover additional species new to science, 12 new species having been published since 2000, a c. 15% increase in numbers for the genus, the recent novelties having been detected mainly in Cameroon (e.g., Onana & Chevillotte, 2015). The range of biological activity shown by these compounds is wide and has great potential to address current and future needs of humanity, from medical to agricultural. However, screening for biological activity lags far behind discovery of compounds.
The case of Vepris teva illustrates the importance of uncovering and publishing species before they become extinct and become lost forever, together with their potential applications for humanity, in this case secondary compounds with potential e.g., as antimicrobials, natural insecticides and in the case of ß-amyrin, recorded here for the first time in Vepris, strong anti-inflammatory action (Okoye et al., 2014).  (Cheek et al., 2020), adding to the estimated 369,000 already documented (Nic Lughadha et al., 2016). However, only 7.2% of species have been assessed for their threat status and are included on the Red List using the IUCN (2012) standard (Bachman et al., 2019). Newly discovered species, such as Vepris teva, reported in this article, are likely to be threatened, since widespread species tend to have been already discovered. There are notable exceptions to this rule (e.g., Vepris occidentalis Cheek & Onana  a species widespread in West Africa from Guinea to Ghana). However, it is generally the more range-restricted, infrequent species that remain unknown to science. This makes it urgent to find, document and protect such species before they become extinct. Until species are described and known to science, it is difficult to assess them for their IUCN conservation status and so the possibility of protecting them is reduced (Cheek et al., 2020). Documented extinctions of plant species are increasing, e.g., in coastal forest of Cameroon, Oxygyne triandra Schltr. is considered extinct at its sole locality, the forest at Mabeta-Moliwe in the foothills of Mt Cameroon (Cheek et al., 2018b;Cheek & Williams, 1999;Cheek, 1992), Inversodicraea bosii (C.Cusset) Rutish. & Thiv. at the Lobe Falls  and in Gabon Pseudohydrosme buettneri Engl. (Cheek, Tchiengué & van der Burgt, 2021) in coastal forest. There are also examples of species that appear to have become extinct even before they are known to science, such as in Cameroon Vepris bali Cheek (Cheek, Gosline & Onana, 2018a), and in Gabon Pseudohydrosme bogneri (Moxon-Holt & Cheek, 2021). Human pressures have been the cause of these extinctions in all these cases.
In the Republic of Congo natural habitat is fortunately relatively extensive and intact, but in some specialised ecosystems such as that with the evergreen thicket on white sand habitat described above, to which Vepris teva is restricted, large areas have entirely disappeared and others are set to follow them.
Further effort in prioritising high priority areas for plant conservation as Tropical Important Plant Areas (TIPAs), using the revised IPA criteria set out in Darbyshire et al. (2017) is being implemented in Guinea (Couch et al., 2019). TIPAs are also in progress in countries such as Cameroon, Ethiopia, Mozambique and Uganda and might be extended elsewhere in Africa such as to the Republic of Congo, to reduce the risk of future global extinctions of range-restricted endemic species such as Vepris teva.
for initially growing Vepris teva from seed, and we thank especially Bradley Gangadeen of the Science Glass for growing it on under the supervision of Joanna Bates who kindly provided cultivation details. The import and safe use of this wild collected plant material was enabled through the use of Defra Plant Health Licence 2149/194627/5. Jean Michel Onana, National Herbarium of Cameroon is thanked for helpful comments on an earlier version of this article, and for formal reviews we also thank Uday Turaga and an anonymous reviewer, together with Whitney Kistler, editor, for their valuable comments which have improved the article.

ADDITIONAL INFORMATION AND DECLARATIONS Funding
The authors received no funding for this work.

Competing Interests
The authors declare that they have no competing interests.

Author Contributions
Moses K. Langat conceived and designed the experiments, performed the experiments, analyzed the data, prepared figures and/or tables, authored or reviewed drafts of the article, and approved the final draft. Teva Kami conceived and designed the experiments, performed the experiments, analyzed the data, authored or reviewed drafts of the article, field collections & observations, and approved the final draft. Martin Cheek conceived and designed the experiments, performed the experiments, analyzed the data, prepared figures and/or tables, authored or reviewed drafts of the article, field observations, and approved the final draft.

Ethics
The following information was supplied relating to ethical approvals (i.e., approving body and any reference numbers): At the Royal Botanic Gardens, Kew, fieldwork was approved by the Institutional Review Board of Kew entitled the Overseas Fieldwork Committee (OFC) for which the registration number was OFC 490-3 -490-6.

Field Study Permissions
The following information was supplied relating to field study approvals (i.e., approving body and any reference numbers): Fieldwork in the Republic of Congo resulting in the specimens and observations cited in this article was conducted with the collaboration and support of the CERVE (Centre d'Etudes sur les Ressources Végétales) (currently named IRSEN (Institut de Recherche National en Sciences Exactes et Naturelles, Brazzaville))-National Herbarium of Congo and Royal Botanic Gardens, Kew beginning in 2010 under research permit (Autorisation de Recherche) 021/MRS/DGRST/DMAST (issued 2 Nov 2010).